ambatovy case study
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Business and Biodiversity Offsets Programme (BBOP)
BBOP Pilot ProjectCase StudyThe Ambatovy Project
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Forest Trends, Conservation International and the Wildlife Conservation Society provided the
Secretariat for BBOP during the first phase of the programme's work (2004 2008).
Publication Data
The Ambatovy Project Business and Biodiversity Offsets Programme Pilot Project Case Study, 2009: TheAmbatovy Project is a Joint Venture project between Sherritt Incorporated, Sumitomo Incorporated, Kores andSNC Lavalin. The Ambatovy Project is comprised of the following two Madagascan operating companies,
Ambatovy Minerals SA (AMSA) and Dynatec Madagascar S.A. (DMSA). The Project Administrative offices arelocated at Trano Fitaratra, 7me tage, Ankorondrano, Antananarivo, Madagascar (PO Box 12085, PosteZoom, Ankorondrano), T: +261 20 22 230 88 / 22 397 35 37 F: +261 20 22 540 30, http://www.sherritt.mg/
Available from www.forest-trends.org/biodiversityoffsetprogram/guidelines/ambatovy-case-study.pdf.
The Ambatovy Project (Ambatovy Minerals SA/Dynatec Madagascar SA) 2009.
Reproduction of this publication for educational or other non-commercial purposes is authorised without priorwritten permission from the copyright holder provided the source is fully acknowledged.
Reproduction of this publication for resale or other commercial purposes is prohibited without prior writtenpermission of the copyright holder.
The findings, interpretations and conclusions expressed here are those of the authors and do not necessarilyreflect the views of The Ambatovy Project. Any errors are purely the responsibility of the authors.
Cover and graphic design by Rima Design.
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THE AMBATOVY PROJECT
BBOP PILOT PROJECT
BUSINESS AND BIODIVERSITY OFFSETSPROGRAMME
CASE STUDYPREPARED BY PIERRE O. BERNER, STEVEN DICKINSON AND ARISTIDE ANDRIANARIMISA
JANUARY 2009
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BBOP Pilot Project Case Study Ambatovy Project
About this document
To help developers, conservation groups, communities, governments and financial institutions that wish to
consider and develop best practice related to biodiversity offsets, the Business and Biodiversity Offsets
Programme (BBOP) has prepared a set of Principles, interim guidance and resource documents1, including
pilot project case studies, of which this Document2is one. All those involved in BBOP are grateful to the
companies who volunteered pilot projects in this first phase of its work.
The ability to test methods and learn from practical experience in a set of pilot projects has played an
important role in the development of the BBOP Principles on Biodiversity Offsets and supporting materials
during the first phase of the programmes work (2004 2008). The Ambatovy Projects four shareholders
volunteered to undertake pilot projects during BBOPs first phase, with some joining at the outset, and some
at later stages. While BBOP has offered some support and technical advice to the individual pi lot projectsthrough its Secretariat and Advisory Committee, each pilot project has been directed and managed by a team
employed or contracted by the companies and city council leading the respective projects. Each of the case
studies prepared by the pilot projects explains the approach taken and how close the Project has come to
completing the design of the biodiversity offset concerned, and sets out the developers current thinking on the
most appropriate offset. This may change as the Project teams finalise their offset programme design and
further implementation. The nature of the guidance used by the pilot projects has varied according to which
drafts of the evolving BBOP Handbooks were available to them at the time. This and the individual
circumstances and context of each pilot project have affected the extent to which they have used or adapted
the BBOP guidance. Consequently, the case studies do not necessarily reflect the range of interim guidance
currently presented in BBOPs Biodiversity Offset Design Handbook, Cost-Benefit Handbook and
Implementation Handbook.
This Document has been provided by the Ambatovy Project subject to the limitations set out herein.
The Ambatovy Project is still working on the design of the proposed biodiversity offset discussed in this case
study. Consequently, none of the suggested or projected activities based on fieldwork to date represent a
commitment on the part of The Ambatovy Project, it shareholders or potential partners to proceed with the
offset as described in draft form in this Document. Such commitment is the subject of continuing internal
discussions. The information and data relating to possible offset sites, areas and activities are presented here
to communicate the initial work that has been done on a potential offset design and to illustrate one possible
approach to the design of a biodiversity offset intended to comply with the BBOP principles.
Where data supplied by external sources, including previous site investigation data, have been used, it has
been assumed that the information is correct unless otherwise stated. No responsibility is accepted by the
Ambatovy Project for incomplete or inaccurate data supplied by others.
1 The BBOP Principles, interim guidance and resource documents, including a glossary, can be found atwww.forest-trends.org/biodiversityoffsetprogram/guidelines/ . To assist readers, a selection of terms with an entry in the BBOPGlossary has been highlighted thus: biodiversity offsets. Users of the Web or CD-ROM version of this document can move theircursors over a glossary term to see the definition.
2 This case study was prepared by Pierre O. Berner, Steven Dickinson and Aristide Andrianarimisa.
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About this document
BBOP Pilot Project Case Study Ambatovy Project
The Ambatovy Project may have retained sub-consultants affiliated with the Ambatovy Project to provide
Services for the benefit of the Ambatovy Project. To the maximum extent allowed by law, users of this
Document acknowledge and agree they will not have any direct legal recourse to, and waive any claim,
demand, or cause of action against, the Ambatovy Projects contractors, sub-contractors, partners,
shareholders and other related or affiliated companies, and their respective employees, officers and directors.
This Document is provided for the use by developers, conservation groups, communities, governments and
financial institutions that wish to consider and develop best practice related to biodiversity offsets. No
responsibility whatsoever for the contents of this Document will be accepted by any person. Any use made of
this Document or any reliance on or decisions to be made based on it, is the responsibility of such users. The
Ambatovy Project accepts no responsibility for damages, if any, suffered by any third party as a result of
decisions made or actions based on this Document.
For greater certainty, this Document has been prepared for the particular purpose outlined herein and no
responsibility is accepted for the use of this Document, in whole or in part, in other contexts or for any other
purpose.
BBOP is embarking on the next phase of its work, during which BBOP hopes to collaborate with moreindividuals and organisations around the world, to test and develop these and other approaches to biodiversity
offsets more widely geographically and in more industry sectors. BBOP is a collaborative programme, and we
welcome your involvement. To learn more about the programme and how to get involved please:
See: www.forest-trends.org/biodiversityoffsetprogram/
Contact: [email protected]
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BBOP Pilot Project Case Study Ambatovy Project
Contents
Table of contents
About this document 1
1. Executive Summary 6
2. Project Context 11
2.1 Policy context 11
2.2 Regional context 12
2.3 Shareholders involved in offset design 14
3. Project Summary 15
3.1 General project description 15
3.2 Ambatovy offset programme 17
4. How the Ambatovy Project is Applying the BBOP Principles 19
5. Current Status of the Project and Offset 24
5.1 Project chronology and status (as of December 2008) 24
5.2 Offset chronology and status (as of December 2008) 24
6. Business Case for a Biodiversity Offset 26
7. The Offset Design Process 28
7.1 Guidance and methodologies used 28
7.2 Roles and responsibility 28
7.3 The offset design process 29
7.3.1 Step 1: Review project scope and activities 29
7.3.2 Step 2: Review the legal framework and / or policy context for a biodiversity offset 29
7.3.3 Step 3: Initiate a stakeholder participation process 29
7.3.4 Step 4: Determine the need for an offset based on residual adverse effects 297.3.5 Step 5: Choose methods to calculate loss / gain and quantify residual losses 35
7.3.6 Step 6: Review potential offset locations and activities and assess thebiodiversity gains which could be achieved at each 46
7.3.7 Step 7: Calculate offset gains and select appropriate offset locations and activities 51
7.3.8 Step 8: Record the offset design and enter the offset implementation process 51
8. Implementation Plan and Long-term Management 53
9. Summary of Offset Process Costs 54
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10. Project Outcomes 56
11. Lessons Learned 58
11.1 Limitations 58
11.1.1 Available data 58
11.1.2 Averaging 59
11.2 Recommendations 59
12. Next Steps 60
13. References 62
Tables
Table 1: Summary of the Ambatovy pilot Project 9
Table 2: Ambatovy Project offset programme 18
Table 3: Summary of attribute weighting (December 2008) 41
Table 4: Azonal habitat (December 2008) 43
Table 5: Transitional habitat (December 2008) 43
Table 6: Zonal habitat (December 2008) 43
Table 7: Pipeline zonal habitat (December 2008) 43
Table 8: Biodiversity loss calculations scenarios at impact site and effect of post-impact remediation 45
Table 9: Summary of estimated costs 54
Table A5.1: Fauna and flora species vulnerability matrix (April 2008) 92
Table A5.2: Key Biodiversity Components Matrix (KBCM) vulnerability scores (April 2008) 92
Graphs
Graph 1: Post-impact mitigation influence on biodiversity loss for forest habitats at impact site 45
Photographs
Photograph 1: Ankerana aerial view 48
Photograph 2: Ankerana azonal habitat 48
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Figures
Figure 1: Project location map 13
Figure 2: Project components map 16
Figure 3: Mine area, showing conservation zones (green) that constitute on-site offset area
(including azonal, transitional and zonal forests) 32
Figure 4: Mine area habitat map 37
Figure 5: Mine footprint and environmental buffer map 37
Figure 6: BBOP benchmark site map 40
Figure 7: Forest habitat percentage hectares loss for the mine component (the pipeline affects onlya small portion of the zonal habitat) 44
Figure 8: Ankerana offsite offset area location and other candidate sites surveyed by the project, inrelation to the Ambatovy mine area 47
Figure 9: Correlation between EVC (azonal, transitional and zonal), substrate and topography 48
Figure 10: Ankerana map 50
Figure 11: Mine area and Analamay-Mantadia forest corridor, allowing link between on-site offset andforest corridor 50
Figure 12: Actions and timings (2004 onwards) 53
Appendices
Appendix 1: Key Biodiversity Components Matrix (KBCM) and Habitat Hectares Score,
December 2008 Iteration 64
Appendix 2: Key Biodiversity Components Matrix (KBCM) and Habitat Hectares Score,February 2008 Iteration 78
Appendix 3: Key Biodiversity Components Matrix (KBCM) and Habitat Hectares Score,April 2008 Iteration 80
Appendix 4: Mine Footprint Status Sheet, 2nd Iteration 87
Appendix 5: Vulnerability Index 91
Appendix 6: Survey for Off-site Azonal Outcrops (in French) 94
Appendix 7: Comparison of Ambatovy / Analamay and Ankerana Azonal Habitats 115
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Executive Summary
BBOP Pilot Project Case Study Ambatovy Project
5. The Torotorofotsy Ramsar wetland ecosystem:the Project is supporting the site management plan
design and implementation in conjunction with government and local NGOs; these efforts aim to ensure
the permanency of legal and managerial commitments in partnership with government and a local NGO.
6. The pipeline right of way reforestation programme:the programme aims at enhancing FOREST
CONNECTIVITYin targeted areas of the Ankeniheny-Zahamena Corridor through expanded reforestation
activities along the slurry pipeline right of way by conducting targeted reforestation in partnership withgovernment and local NGOs.
7. The mine footprint replacement forest:the Project aims to create a replacement, multifunctional
forest on the footprint during progressive reclamation with an established, integrated managerial
structure by mine closure.
The Ambatovy offset programme design approach was tailored according to the guidelines provided by the
BBOP Secretariat and Advisory Committee. It includes the following steps:
Step 1. Reviewing the offset project scope and activities:the offset project was outlined in the
ENVIRONMENTAL AND SOCIAL IMPACT ASSESSMENT(ESIA), to go above and beyond the expected
regulatory requirements, and was presented during stakeholder consultation; the Project became apilot project in 2006 before obtaining its operating permit.
Step 2. Reviewing the legal policy context for its biodiversity offset programme:key elements
comprise the MECIE decree (Mise en Compatibilit des Investissements avec l'Environnement,
Decree N 2004-167 modified), the Madagascar Action Plan (MAP) 2007 2012, the regional and
communal development plans and the EQUATOR PRINCIPLES.
Step 3. Initiating stakeholder participation: PARTICIPATIONhas been pursued since the ESIA stage,
engaging the Projects shareholders, government, financiers, NGOs and local communities in the
design of the offset programme and integrating their feedback.
Step 4. Determining the need for an offset based on residual adverse effects : the Projects principal
impacts on natural systems and biodiversity were assessed by the project ESIA. DIRECT IMPACTS
were predicted to occur at the mine area through the phased clearing of the 1,336 ha mine footprint
within an ecologically sensitive semi-pristine forest mosaic. The KEY BIODIVERSITY COMPONENTSin
the mine area and upper slurry pipeline portion include significant numbers of fauna (16 lemurs, 62
birds, 123 herpetofauna), fish and 376 flora species, three structurally distinct HABITAT TYPESand a
landscape-level habitat assemblage with functional interactions between its forest habitats. A very
substantial MITIGATIONprogramme was implemented through the Ambatovy Projects Biodiversity
Management Plan (BMP). The Projects most significant RESIDUAL IMPACTSoccur at the mine site,
including both direct impacts through the clearing of the 1,336 ha footprint (and associated
biodiversity) and indirect residual impacts from edge effects on the environmental buffer (790 ha).Other key Project components are located in areas that are already heavily and historically
degraded and thus have negligible negative impacts on biodiversity.
Step 5. Methods to calculate LOSSES/ GAINSand quantify residual losses: the Project used the BENCHMARK
and HABITAT HECTARESmethodology to determine the scale of the offset needed to achieve the
CONSERVATION GAINSthat will achieve no net loss of biodiversity. The Project will generate a total loss
of 1,168 habitat hectares that any offset will be required to compensate; this result will be refined with
complementary fauna quantitative data acquired in early 2009. Socioeconomic losses and
compensations from the offset programme will be determined during 2009.
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Step 6. Reviewing potential offset locations and activities to assess biodiversity gains which could
be achieved: preliminary surveys of offset candidate sites were undertaken in 2005 with the
objective of identifying potential IN-KINDtype offsets. The Ankerana forest site has many similarities
with the Ambatovy mine site forests, supporting the hypothesis that Ankerana can be considered in-
kind relative to the Ambatovy azonal habitats.
Step 7. Calculating offset gains and select appropriate offset locations and activities : additional work
to verify Ankeranas similarities is required and planned for 2009, including detailed quantification of
potential offset gains. Gains from other offset programme components will also be calculated and
integrated.
Step 8. Recording the offset design and entering the offset implementation process: the Ankerana
offset design and other components of the offset programme have not yet been finalised, thus the
implementation process has not formally begun. The Project will finalise the offset programme
design, using BBOP guidance, during the course of 2009.
The team plans to complete the design of the offset programme implementation plan by the end of 2009, with
the Ankerana and other offset sites gain calculated in 2010, and thus the final offset design completed at thatpoint. The Project will have the responsibility of ensuring the management of the Ankerana site, while actual
site protection and local management will likely be entrusted to an NGO. For Ankerana, the annual
operational costs are in the process of being established and are estimated to be in the range US$ 250,000
300,000 per annum. Since the offset programme is still in the design phase, the actual conservation outcomes
to date are limited. They represent what the Project has achieved thus far and the benefits the Project has
already enjoyed and include securing the temporary protection of Ankerana until the Ministerial decree for its
protection is finalised; integrating Ankerana into the national protected areas network; coordination between
government organisations, NGOs, local communities and the private sector; local community awareness and
reforestation activities. At the mine site, forest and TAXA-specific conservation management plans were
developed for flora and fauna, (e.g., lemurs, Mantella frog species and fish). Although these programmes
were developed as part of the Biodiversity Management Plan, their importance is reinforced by their aim of
ensuring the conservation of azonal habitat and associated species, thus ensuring that all key biodiversity
components present on the IMPACT SITEare present at the offset.
A summary of the Ambatovy Project pilot project BBOP programme is presented in Table 1.
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Table 1: Summary of the Ambatovy pilo t Project
Company name Ambatovy Minerals SA & Dynatec Madagascar SA (AMSA / DMSA)
Project name Ambatovy Project Madagascar
Sector &
project
description
Ambatovy is a large-tonnage nickel Project with an annual design capacity of 60,000 tonnes of
nickel, 5,600 tonnes of cobalt and 190,000 tonnes of ammonium sulphate. Production is scheduled
to begin in 2010, with full capacity expected to be achieved by 2013. The Projects assessed reserve
life is 27 years, with potential for extension beyond this. The main impacts to biodiversity are located
at the mine footprint with the clearing of near-primary forest. The Project has designed and
implemented a Biodiversity Management Programme to mitigate and monitor the residual impacts
associated to development, whilst pursuing its impact AVOIDANCEand reduction approach. The
mitigation measures cover flora, fauna and aquatics.
Country Republic of Madagascar (Alaotra Mangoro and Atsinanana regions, eastern Madagascar).
Shareholders Sherritt International Corporation, Sumitomo Corporation, Kores, and SNC Lavalin Incorporated.
Principal
biodiversitycomponents
affected by
Project
The key biodiversity components, mostly confined to the mine area and upper slurry pipeline portion,
can be summarised as follows: Priority species:
16 lemurs species, including Prolemur simus(IUCN CR), Propithecus d. diadema(IUCN
EN), Indri indri(IUCN EN), Eulemur rubriventer(IUCN VU), Daubentonia madagascarensis
(IUCN NT), Hapalemur griseus(VU),Allocebus trichotis(IUCN DD);
62 birds species, including Tyto soumagnei, Anas melleriandArdea humbloti, Sarothura
watersi(IUCN EN);
123 herpetofauna species, including Mantella aurantiaca(IUCN CR), M. crocea(IUCN EN)
and Sanzinia madagascariensis(IUCN VU);
5 fish species of which Rheoles alaotrensis(IUCN VU) and at least two new Ratsirakia
species;
24 insect species, which are considered rare at a national level;
376 plants includingAsteropeia mcphersonii(IUCN VU), Leptolaena multiflora(IUCN EN),
Dalbergia baroni(IUCN VU) and 330 species of concern, which are considered rare in
Madagascar;
Three structurally distinct habitat types: zonal, transitional and azonal forests (the latter including
seasonal ponds and upper watershed stream systems) and their fauna and flora communities;
and
The landscape-level habitat assemblage with the functional interaction between the zonal,
transitional and azonal forests.
Scale of impact The main anticipated residual impacts on biodiversity caused by the Project will occur at the mine
site and in the upper portion of the slurry pipeline through the progressive clearing of the mine
footprint (approximately 1,336 ha), located within an ecologically sensitive natural forest mosaic ofthe eastern mid-altitudinal forest corridor. Stringent impact avoidance and minimisation strategies
were applied in the design phase of the Project. Residual impacts on biodiversity at the other Project
components are insignificant due to human-induced degradation in these areas but will nonetheless
be offset. These include pipelines, the processing plant, the tailings area and a pier extension
project.
The 218 km of buried slurry pipelines will involve the clearing of a mix of native and non-native
secondary vegetation resulting from historical slash and burn with comparatively little biodiversity
value. However, two sections of the pipeline cross sensitive habitats: the first 2 km of zonal, near-
primary forest accounted for in the mine footprint and the crossing of the Ankeniheny-Zahamena
Corridor at Vohimana, where the pipeline has been routed to avoid residual primary forest fragments.
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Executive Summary 1
BBOP Pilot Project Case Study Ambatovy Project
The processing plant occupies 2.6 km2of the Toamasina industrial zone. The associated tailings
system of 14 km2will be located in a highly degraded agricultural matrix. An existing pier at the
harbour will be extended by over 300 m to accommodate the Projects logistical needs. The
processing plant, tailings and pier extension have been assessed in the Environmental and Social
Impact Assessment (ESIA) to have negligible residual impacts on biodiversity.
As the Project is developing the ESIA is being revisited to ensure that no residual impact to
biodiversity is being neglected. Any further residual impacts identified will be accounted for in thebiodiversity offset calculation.
Description o f
offset
The Ambatovy offsets programme is multifaceted with many components. The Ambatovy Project is
committed to achieve positive conservation outcomes through designing and implementing its
multifaceted programme, that includes:
1. Ankerana offset :establishing an 11,600 ha endangered forest off-site offset, with similar abiotic
and biotic conditions to those found at the mine site and ensuring long term protection through
legal arrangements and community consensus.
2. Azonal forest sites: establishing two on-site (mine) azonal forest habitats conservation areas
that occur partially over the mine footprint and ensuring long term protection through legal and
managerial commitments.
3. Mine area conservation forest:establishing a 4,900 ha conservation forest area around thefootprint and ensuring long term conservation as part of the priority species management
programme and maintenance of the ecological services for the local communities.
4. Analamay-Mantadia forest corr idor :spearheading the establishment of a forest corridor
between the mine area forests and the nearby Ankeniheny-Zahamena Corridor and securing
long term landscape level connectivity for the protection of mine area biodiversity through
partnerships with government, NGOs and local communities.
5. Torotorofotsy Ramsar:supporting the site management plan design and implementation in
conjunction with government and local NGOs and ensuring permanency of legal and managerial
commitments with its partnerships.
6. Pipeline right of way reforestation:enhancing forest connectivity in targeted areas of the
Ankeniheny-Zahamena Corridor through expanded reforestation activities along the slurry
pipeline right of way and conducting targeted reforestation in partnership with government andlocal NGOs.
7. Mine footprint replacement forest:creating a replacement, multifunctional forest on the
footprint during progressive reclamation with an established, integrated managerial structure by
mine closure.
While the design and implementation of the several components of the Ambatovy offset programme
has progressed, the predicted conservation outcomes from these various offset components have
not yet been fully calculated. Meanwhile, Ambatovy has focused on its proposed Ankerana offset as
the most significant component of its offset. However, the high degree of social sensitivity around
Ankerana has led the project to undertake community involvement before the planned biodiversity
assessment at the site. The impact of the first pipeline section will be included in the offset
calculation for the mine site. The second section of pipeline will be offset by reforestation not only of
the pipeline footprint but also of broader areas with the aim of reconnecting the forest corridor.
Links to further
information
http://www.sherritt.com and http://www.sherritt.mg
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BBOP Pilot Project Case Study Ambatovy Project
2. Project Context
2.1 Policy context
Investment projects in Madagascar must be compatible with Malagasy environmental regulations. This
principle is embedded in the MECIE (Mise en Compatibilit des Investissements avec l'Environnement)
decree (DecreeN 2004-167 modified). The application of this decree is enforced by the environmental
regulator, ONE (Office National de lEnvironnement), which has developed stringent guidelines and protocols
on how to elaborate, review, permit and monitor Environmental and Social Impact Assessments (ESIA).
Although the terms of reference for an ESIA in Madagascar typically require stringent mitigation of impacts,
biodiversity offsets are not included in the text.
The Government of Madagascar became aware of biodiversity offset mechanisms through interactions withenvironmental NGOs in 2005 (WWF, Conservation International CI, Wildlife Conservation Society WCS).
Subsequently, the BBOP Secretariat attended a presidential audience to discuss biodiversity offsets in June
2006 during which the concept of offsets as a complementary mechanism to reduce impacts on Madagascars
heritage was well received by the President of Madagascar. Biodiversity offsets were subsequently referred to
in the Madagascar Action Plan (MAP) 2007 2012:
Commitment # 7 Cherishing the Environment
Challenge # 3 Develop the Environmental Reflex at All Levels"
Priority Projects and Activities # 3 Develop a policy for mining companies and logging companies for
biodiversity offsetsand other mechanisms and incentives for environmental protection
The ESIA for the Ambatovy Project (MINEVEF/ONE Permit # 47/06 dated December 1st, 2006) established
that the Project, and specifically the mine component, would be located in a sensitive biodiversity area and
that the mitigation of residual impacts would require both on-site and off-site compensation measures. While
on-site measures at the mine are commitments made in the ESIA, the Ambatovy offset programme goes
above and beyond compliance with legal obligations. The offset programme is believed to deliver positive
conservation outcomes under a vision of no net loss of biodiversity, and possibly net gain. This would enable
the Project to honour its stringent biodiversity policy developed and endorsed by its shareholders:
to cause no net harm to biological diversity where we operate, to mitigate unavoidable impacts, and to
practice responsible closure procedures;
to assure the conservation of habitats, flora and fauna, using all reasonable actions and technologies;
to ensure responsible attention to the maintenance and, where possible, enhancement of biodiversity in
the best interest of our business, the communities in which we operate, and the world at large.
The Projects principal financial lenders have subscribed to the Equator Principles (http://www.equator-
principles.com/index.shtml ). In this context, full regulatory compliance and the implementation of a thorough
impact management strategy is expected. In addition, the lenders also require the Projects general
compliance with the IFC Performance Standards and specifically Performance Standard 6 (Biodiversity
Conservation and Sustainable Natural Resource Management). In the context of biodiversity offsets,
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Project Context 1
BBOP Pilot Project Case Study Ambatovy Project
paragraph 8 of Standard 6 is particularly relevant and requires the design of mitigation measures to achieve
no net loss of biodiversity where feasible. These measures may include a combination of actions, such as:
Post-operation restoration of habitats
Offset of losses through the creation of ecologically comparable area(s) that is managed for biodiversity
Compensation to direct users of biodiversity
The Project is thus designed to comply with the IFC Performance Standards for major projects.
2.2 Regional context
The Ambatovy Project has six components, including the mine, the slurry pipeline, the processing plant
(including refinery), the tailings management facility, the harbour extension and resettlement sites (see Figure
1). The Project covers a large territory extending over two of Madagascars twenty-two regions (Alaotra-
Mangoro and Toamasina). The mine is located at an elevation of approximately 1,000 m above sea level
(m.a.s.l.), near the town of Moramanga. The industrial complex (plant, tailings management facility andharbour) is located 130 km to the northeast of the mine site, in the seaport city of Toamasina. A slurry pipeline
carrying a water laterite slurry, which contains the ore, links the mine and plant. The proposed Ankerana
offset, constituting the key component of the multifaceted offset programme, is situated in a very remote area
between the mine site and Toamasina.
As presented in the Project ESIA, the principal biodiversity sensitivities of the Project are concentrated in the
forested mine area and within the upper portion of the slurry pipeline, while social issues are relevant for all
components. Biodiversity resources within the mine region have strong intrinsic and USE VALUESand
communities there largely depend on these biodiversity resources for their LIVELIHOODS. However, in light of
current agricultural practices and population growth, natural resource and biodiversity utilisation by local
communities is far from sustainable in the mine region; the depletion is such that this natural capital will not be
available to future generations unless fundamental changes take place. The socioeconomic impacts on the
local communities from the Projects offset programme will need to be considered. The mitigation of these
impacts needs to be designed in the context of national, regional and communal plans that address long-term
issues of sustainable resource use in the regions in which the Project operates.
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Project Context 1
BBOP Pilot Project Case Study Ambatovy Project
Figure 1: Project location map
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Project Context 1
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2.3 Shareholders involved in offset design
Shareholders: the Project is jointly owned by Sherritt Incorporated, Sumitomo Incorporated, Kores and
SNC Lavalin. Each partner has played an important role in the Projects environmental programme,
including regulatory compliance, impact mitigation, risk management and design of a comprehensive
biodiversity offset programme. The Ambatovy vision, besides the goal of generating attractive economicresults, is to contribute significantly to the host country and to deliver outstanding safety, social and
environmental performance.
Government: the general offset principle is captured in the MAP (see Policy Contextsection above) and
specific governmental entities have been involved in the offset design, including the Ministry of
Environment, Water, Forests and Tourism (MEWFT) and the Malagasy Forest Service, which have actively
participated in securing the proposed offset site at Ankerana via a community-led zoning process.
Lenders: the Ambatovy Project is one of the largest capital investment projects in the world and it is
financially supported by a number of lender banks, most of which have adopted the EQUATOR PRINCIPLES.
Lenders includes the African Development Bank (AFDB), Export Development Canada (EDC), Export-
Import Bank of Korea (K-EXIM), the European Investment Bank (EIB), the Japan Bank for InternationalCooperation (JBIC) and various commercial banks such as Socit Gnrale and BNP Paribas. The
consideration of Performance Standard 6 in the Projects Biodiversity Management Plan, including the
taxa-specific plans, reflects this.
NGOs: environmental NGOs in Madagascar are aware of the offset concept and are encouraging the
Ambatovy Project to continue moving its offset programme forward in an effort to ensure NO NET LOSSon
biodiversity and, preferably, net gain. However, it is worth noting that some STAKEHOLDERSvoice concerns
about the Projects ability to deliver no net loss of biodiversity and are closely scrutinising the Projects
offset initiative. Given this, the Project has been actively working to enhance its offset programme in
collaboration with NGOs such as CI, WCS and ERI (Eco Regional Initiative). A number of other NGOs
working with the Ambatovy Project on impact mitigation have also provided valuable input to the offset
design process (e.g., Groupe dEtudes et de Recherche des Lmuriens, Henry Doorly Zoo and itsMadagascar Biodiversity Program, Madagasikara Voakajy, Missouri Botanical Garden, Mitsinjo, University
of Antananarivo Biology department, the South African Institute of Aquatic Biology, WWF and others).
Local communities: the Project continues to engage stakeholders, including local communities, to ensure
that any offset is compatible and integrated with regional and local land and resource management visions.
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3. Project Summary
3.1 General project description
The Ambatovy Project is a large-tonnage nickel project with an annual design capacity of 60,000 tonnes of
nickel and 5,600 tonnes of cobalt. Additionally, the Project will produce 190,000 tonnes of fertiliser
(ammonium sulphate) as a by-product from the refinery, a product much needed in this part of the world.
The Project was permitted in December 2006 and construction began in early 2007. Production is due to
begin at the end of 2010, reaching full capacity by 2013. Based on proven nickel and cobalt ore reserves, the
Projects expected lifecycle is 27 years, although operation beyond this is likely, as stored low-grade ore could
become an economic commodity in the future.
The locations of the main Project components are shown in Figure 2, and the key features are summarised below:
The Ambatovy mine lies within the mid-altitude forests, at the westerly limit of the residual eastern rain
forest known as the Ankeniheny-Zahamena Corridor. The near-primary forests of the mine area have
undergone considerable human-induced pressures including hunting and gathering, selective logging,
slash and burn agriculture, uncontrolled fires and species collection for trade;
The slurry pipeline, buried over the majority of its route, will pass through 2 km of near-primary forest
surrounding the mine, crosses a Ramsar site (avoiding the wetlands by following an old railroad spur) and
traverses the Ankeniheny-Zahamena forest corridor by avoiding residual forest fragments whenever
possible. It then continues to the coast through hilly terrain of the former eastern rain forest destroyed by
extensive slash and burn agriculture; The industrial complex, including the processing plant and the refinery, the tailings and the harbour, is
located within an anthropogenic coastal landscape in a suburban setting. The plant and harbour lay within
the industrial zones of Toamasina; and
The proposed Ankerana offset site, which is equidistant between the mine and Toamasina, is a large,
mountainous dome covered with primary forest, encroached only by slash and burn agriculture in
surrounding valleys where frontier dwellings exist. The pristine character of the site is a result of its
remoteness and the low density of surrounding human populations.
The Projects principal impacts on natural systems and biodiversity will occur at the mine area, through the
phased clearing of the mine footprint within an ecologically sensitive natural forest mosaic. The sensitivity of
this mosaic arises from the considerable local heterogeneity in terms of geology, geomorphology, substrate,
topography and meso-climate.
It is widely documented that the average annual deforestation rate calculated over the period between 2000
and 2005 was 0.35%. In total, between 1990 and 2005, Madagascar lost 6.2% of its forest cover,
approximately 854,000 ha. The current annual loss of the residual eastern rain forest is equivalent to 14,000
ha per year. The total mine footprint to be cleared (1,336 ha) represents only 0.03% of the residual eastern
rain forest, estimated in 2008 at 4,012,100 ha. In consideration of the large forest loss in eastern Madagascar,
the INTRINSIC VALUEof the offset area at Ankerana (11,600 ha) will increase over time as such forest estates
and their associated biodiversity become rarer.
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Figure 2: Project components map
While the bulk of the residual biodiversity impact will arise in the mine area and in the upper portion of the
pipeline, the Projects offset calculation considers residual impacts from each project component including the
entire slurry pipeline, the processing plant, the tailings and the harbour extension. The intention is that all
residual impacts will be offset.
Approximately 90% of the pipelines 218 km right of way will require the clearance of secondary, non-sensitive
and mostly non-ligneous vegetation, which has resulted from historical slash and burn and has comparatively
little biodiversity value. Disturbed land will ultimately be rehabilitated using species appropriate to current land
use in the different pipeline sectors (including provision of fuel wood species to reduce pressure on native
forests). However, two sections of the pipeline cross sensitive habitats:
The first 2 km of zonal, near-primary forest at the mine area; these losses are integrated to the mine
footprint loss calculations; and
The Ankeniheny-Zahamena forest corridor area, which led to 16.5 ha of zonal forest being cleared, despite
planning and routing efforts to avoid the residual primary forest fragments present there.
The processing plant, currently under construction, covers 2.6 km2of Toamasinas industrial zone. The
tailings management facility has a footprint of 14 km2and is located in a highly degraded, fire-driven
agricultural matrix, where irreversible, human-induced depletion of the original biodiversity occurred during
historical forest clearance. The harbour expansion requires the construction of an extended pier (over 300 m)
to accommodate the unloading of equipment during the construction and the importation of raw material (coal,
sulphur, limestone and diesel) and the loading of nickel and cobalt briquette bags and ammonium sulphate
during operation. At the Projects industrial complex (plant, tailings management facility and harbour), most of
the biodiversity values were lost many years ago through extensive habitat conversion. The Projects ESIA
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notes that the industrial complex will have negligible residual impacts on biodiversity, which will nonetheless
be traded up through the Projects offset programme.
Specific aspects of the biological environment assessed in the ESIA are being revisited through expanded
BASELINE STUDIESto ensure that residual impacts are fully documented and included in the biodiversity offset
calculation.
The KEY BIODIVERSITY COMPONENTSin the mine area and upper slurry pipeline portion can be summarised as:
Priority species, with home ranges overlapping (and or potentially overlapping) the mine footprint:
16 lemurs species, including Prolemur simus (IUCN CR), Propithecus d. diadema (IUCN EN), Indri indri
(IUCN EN), Eulemur rubriventer (IUCN VU), Daubentonia madagascarensis (IUCN NT), Hapalemur
griseus (VU), Allocebus trichotis (IUCN DD);
62 birds species, including Tyto soumagnei, Anas melleri and Ardea humbloti, Sarothura watersi (all
IUCN EN);
123 herpetofauna species, including Mantella aurantiaca (IUCN CR),M. crocea (IUCN EN),Sanzinia
madagascariensis(IUCN VU);
5 fish species of which Rheoles alaotrensis(IUCN VU) and at least two new Ratsirakiaspecies;
24 insects species, which are considered rare at a national level;
376 plants includingAsteropeia mcphersonii (IUCN VU), Leptolaena multiflora (IUCN EN), Dalbergia
baroni (UCN VU) and the 330 species of concern which are considered rare in Madagascar;
Three structurally distinct HABITAT TYPES: zonal, transitional and azonal forests (the latter including
seasonal ponds and upper watershed stream systems) and their fauna and flora communities; and
The landscape-level habitat assemblage with the functional interaction between the zonal, transitional and
azonal forests.
Section 7.3 presents more detail in the form of a Key Biodiversity Components Matrix (KBCM) and the steps
followed in its completion. The full KBCM (December 2008 iteration) is provided in Appendix 1. Earlier
iterations (February and April 2008) are presented in Appendices 2 and 3 respectively.
3.2 Ambatovy offset programme
The Ambatovy Project offset programme is a multifaceted endeavour to achieve measurable CONSERVATION
OUTCOMESresulting in no net loss and preferably a NET GAINof biodiversity. It has been adopted voluntarily to
go above and beyond the Projects impacts management strategy. The Ambatovy Project intends to
implement its diversified offset portfolio, as presented in Table 2.
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Table 2: Ambatovy Project offset programme
#Offset
componentDesign Implementation
1 Ankerana Establishing a large off-site offset site atAnkerana, encompassing similar ABIOTIC
and BIOTICconditions to those found atthe mine site. The site is located 71 km tothe northeast of the mine site and wouldinvolve conservation of 11,600 ha ofendangered forest, including a multipleuse area of 7,000 ha and a coreconservation area of 4,600 ha, withinwhich there is a large tract of azonalforest.
Ensure long term protection of the Ankerana offsetsite through the stringent legal arrangements and
strong community consensus. Communitymotivation and consent is the highest priority of theAmbatovy Project offset implementation in its earlyphase and needs to be obtained before theBIODIVERSITY INVENTORIESare conducted (perceivedas external intrusions by the local communities if illprepared). Adhere to BBOP principles andguidelines for offset processes. Monitoring ofefficacy of BBOP tools used and offset programmeevaluation in 2011 and option analysis.
2 Azonal forestsites
Protecting, for the long term, two on-siteconservation sites of the azonal foresthabitats that occur partially over the minefootprint that would otherwise be lost todeforestation.
Ensure permanency of on-site conservation azonalsites through legal and managerial commitments.Ensure permanency of surrounding mine areaforests (see offset component #3) with samemeasures as mentioned above. Ensure connectivityof mine area forests with surrounding protectedareas (see offset component #4).
3 Mine areaconservationforest
Ensuring long term conservation of theforest surrounding the mine footprint aspart of the priority species managementprogramme and maintenance of theecological services for the localcommunities. The area consists of theestablishment of 4,900 ha of buffer forestaround the footprint.
Conduct multifunctional zoning based on existingmodels in Madagascar and ensure management ofleased lands and in areas of targeted communitytransfer. It is believed that site that would otherwisebe lost given regional deforestation rates.
4 Analamay-
Mantadiaforest corridor
Promoting the landscape level
connectivity of the mine area forests withthe nearby Ankeniheny-ZahamenaCorridor to secure long term protection ofmine area biodiversity as part of theDurban Vision implementation.
Enter into formal partnerships with government,
NGOs and local communities to design and developimplementation plans for the Analamay-MantadiaCorridor, that take present and future communityneeds into account.
5 TorotorofotsyRamsar
Supporting the Torotorofotsy Ramsar sitemanagement plan design andimplementation in conjunction withgovernment and local NGO.
In partnership with government and local NGO,ensure permanency of legal and managerialcommitments. In a first phase, complete zoning andmanagement plan for Ramsar site. Development ofpragmatic viable resources uses to maintainecological functions of wetland area whilecommunity needs are met.
6 Pipeline right
of wayreforestation
Enhancing FOREST CONNECTIVITYin
targeted areas of the Ankeniheny-Zahamena Corridor through expandedreforestation activities along the slurrypipeline right of way.
In partnership with government and local NGOs
conduct targeted reforestation of the Ankeniheny-Zahamena Corridor (CAZ) with the aim of re-establishing forest connectivity.
7 Mine footprintreplacementforest
Creating a replacement, multifunctionalforest on the entire footprint duringprogressive reclamation with anestablished, integrated managerialstructure by mine closure.
Design and implement management plans forengineering, water management, erosion control,early vegetation establishment, targeted speciesreforestation, induced and facilitated secondarysuccessions and sylviculture treatments.
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4. How the Ambatovy Project isApplying the BBOP Principles
During the ESIA in 2004 and 2005, the Ambatovy Project initiated its offset programme based on an improved
understanding of RESIDUAL IMPACTSand the need for developing compensatory conservation activities. In
2006, Ambatovy became a BBOP PILOT PROJECTand refined its initial offset vision and the design approach
was tailored according to the guidelines provided by the BBOP Secretariat and Advisory Committee.
The BBOP PRINCIPLES ON BIODIVERSITY OFFSETSwere finalised in December 20083, following several years of
groundwork including the development of draft guidance and tools. The Projects offset initiative was
developed alongside, and is generally well-aligned with, the BBOP Principles. The Projects alignment with the
BBOP Principles is illustrated in more detail in Section 7. The Project applies the BBOP Principles as follows:
1. No net loss:
The Projects aim is to achieve measurable conservation outcomes that deliver NO NET LOSSof biodiversity
and a possible net gain through a mix of complementary offset and mitigation activities, including:
An offset site at Ankerana that contains a core conservation area designed to compensate for the Projects
residual impacts on azonal forest biodiversity.
Protection of viable tracts of azonal forest habitats through the set-aside of two specific on-site azonal
forest habitat conservation zones within the forests surrounding the mine footprint (see next point).
Implementation of a no species EXTINCTION commitment and protection of forests surrounding the mine
footprint to ensure the long-term viability of priority species populations impacted by the Project. This
approach would include the on-site azonal forest habitat conservation zones and mechanisms to control
current human pressure on these areas.
Design and implementation of protection measures for an existing residual forest corridor linking forests
surrounding the mine area and the Mantadia National Park to ensure landscape-level forest connectivity.
Targeted reforestation of the Ankeniheny-Zahamena Corridor, in partnership with government and local
NGOs, to re-establish forest connectivity between Mantadia National Park and the Man and the Biosphere
Private Reserve.
Development of the Ramsar Torotorofotsy Management Plan in partnership with government and localNGOs, and contribution to its subsequent implementation.
Progressive rehabilitation at the mine site to produce a multifunctional replacement forest with reinstated
biodiversity values to be included in the offset calculation.
To date, the Projects offset planners have used BBOP guidance and methodologies to assess the impact on
biodiversity and to identify potential sites for biodiversity offsets. BBOP methodologies will also be followed to
3 The full text of the BBOP Principles is available in the BBOP document Business, Biodiversity Offsets and BBOP: An Overview see www.forest-trends.org/biodiversityoffsetprogram/guidelines/overview.pdf.
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determine the scale of the offset required to deliver no net loss, to verify that no net loss has been achieved
and to define implementation measures that will ensure the long-term sustainability of the offset.
2. Additional conservation outcomes:
The Project is designing and implementing conservation activities that are predicted to deliver ADDITIONALITY,
as summarised below for each of the Projects components:
The proposed Ankerana offset site is currently being integrated within the recently established SAPM
(National Protected Areas System) under the Durban Vision. However, there is a significant shortfall in the
financial and human resources to offer protection to all these areas and the Durban Vision can only be
implemented if an array of different partners commits to developing the required financial and human
resources. Through the proposed offset, the Project will play a role in that development process.
Historically the azonal forest habitats of Ambatovy and Analamay have suffered significant anthropogenic
impacts(e.g., from hunting and gathering, destructive honey collection, fire, charcoal, slash and burn, and
the pet trade). The long-term survival of this habitat in the absence of the Project is far from proven. This is
clearly seen in the baseline data for the mine area: of the total area of 1,347 ha of azonal forest habitat in
the mine area, only 60% is of prime quality, the rest being significantly degraded before the project wasestablished. While the mine development is predicted to impact 590 ha of prime quality azonal forest
habitat, 212 ha (26.4% of the total prime quality habitat) will be preserved through the Projects on-site
azonal habitat conservation initiative. The likelihood of successful conservation of a viable portion of the
unique azonal forest habitat at Ambatovy is therefore significantly increased by the presence of the Project.
Similarly, the zonal forests surrounding the mine footprint have experienced historic anthropogenic impacts
such as forest structure modification (logging), species composition modification though canopy openings
(invaders, heliophytes), FOREST FRAGMENTATIONthrough clear cutting, and plain, irreversible loss of forest
areas. The Project has committed to preserving the residual forests of the mine area by, for example,
implementing forest community transfer4to avoid further anthropogenic losses. Such additionality, if clearly
established, will be included in the offset calculations once data and a model for the rate of regionaldeforestation are available.
In the long-term, the forests of the mine area and Mantadia National Park are likely to become isolated
unless the existing forest corridor that links these areas is managed and protected. The loss of this corridor
would cause landscape-level forest fragmentation and jeopardise the long-term viability of populations of
critical species that the project has committed to protect at the mine area. As of December 2008, the forest
corridor has not been included in the first zoning approximation of the Durban Vision. The Project and its
partners plan to create a westerly extension of the Durban Vision zoning to incorporate this area in the
protection zone of the Ankeniheny-Zahamena Corridor. Forest loss avoidance via the successful
management and protection of the corridor will be taken into account in offset calculations based on a fair
assessment of the resulting additionality.
The Ramsar Torotorofotsy site is experiencing considerable pressure from inward migration, the drainage
of wetlands and subsequent conversion to rice paddies, wildfires, slash and burn activities in the forested
watersheds, hunting and the pet trade. The National Committee on Ramsar (CONARAMS) has given a
local NGO (Mitsinjo) the mandate to design and implement a management plan. Ambatovy has joined this
effort as a partner and will work with Mitsinjo and others to enhance the management plan. The first step
4 The targeted forest areas are jointly managed with local communities, using a defined management programme that meetsconservation and sustainable use requirements.
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will be to establish a functional zoning that results in the avoidance of BIODIVERSITY LOSS, which will be
taken into account in offset calculations, again based on a fair assessment of the resulting additionality.
Reforestation activities to reconnect residual patches of primary forests at the perimeter of the slurry
pipeline right of way within the Ankeniheny-Zahamena Corridor will contribute to an overall corridor
defragmentation. The areas to be reforested sit outside of the SAPM and will be accounted for in the offset
GAINcalculation as clearly additional outcomes.
3. Adherence to the mitig ation hierarchy:
Given the Projects setting (high regional biodiversity and endemicity), rigorous biodiversity management is
necessary to meet its policy of no net harm to biodiversity. Before considering biodiversity offsets, the
Ambatovy Project implemented appropriate avoidance and minimisation measures according to the
MITIGATION HIERARCHY, for example:
AVOIDANCE: analysis of pipeline route alternatives, including the study of 21 major re-routes to avoid
ecologically, socially and culturally sensitive areas; avoidance of other sensitive areas during the
development of other Project components whenever possible. Also, set-aside of an area of the ore body
that would otherwise be mined as the foundation of the on-site azonal habitat conservation initiative.
Minimisation: reduction of the surface area subject to impacts through appropriate design and
implementation.
Early (2004 / 05) impact mitigation through the rehabilitation of 50 km of exploration roads and
platforms in the mine area.
Mitigation of impacts following forest clearance through biodiversity rescue and management programs
(lemurs, small mammals, herpetofaunaand fish).
Management of surges in total suspended solids to protect water quality and aquatic biodiversity in
seven affected watersheds downstream of the mine site using large retention dams (at a cost of US$ 40
million).
Restoration / rehabilitation: planned progressive rehabilitation of the mine site footprint to create a
replacement forest with reinstated biodiversity values and reduce the net residual impact.
4. Limit s to what can be offset:
The Ambatovy Project currently believes that all its direct residual impacts on biodiversity are OFFSETABLE. No
habitat or species (flora and fauna) ENDEMICto the mine footprint alone have been identified during the
thorough investigations to date. Nevertheless, given the high levels of biodiversity and endemicity around the
Project, field studies will continue as the mine is developed and forest clearance progresses.
In contrast, the Project believes that there are limits to offsetting certain social impacts. For local communities,there were few legal and cultural constraints on the exploitation of natural resources and biodiversity prior to
the arrival of the mine. In light of forest clearance during development of the mine and the Projects
commitment to conserve the surrounding forests by introducing a zoned approach to forest use, the local
communities existing way of life, including unsustainable use of biodiversity, will undoubtedly be disrupted.
The Ambatovy Project believes that this disruption cannot be entirely offset and also that, in light of dwindling
forest resources and population growth, it is desirable from a BIODIVERSITY CONSERVATIONperspective to seek
to break the cycle of unsustainable use by local communities and replace it with a more sustainable model.
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The present unfettered community exploitation of resources may reflect a lack of community empowerment
and choice. Hence, the changes envisioned by the Project (sustainable, participatory forest use) may
ultimately be viewed by local communities as a positive transformation relative to the current situation.
The same concept applies to the Ankerana offset site where the Project believes that the pre-project
socioeconomic conditions should not be, and ultimately cannot be, maintained. While this change can also not
be offset, the Project believes the change to sustainable use of natural resources will ultimately be to the
benefit of both local communities and biodiversity.
5. Landscape context:
The spatial spread of the Project has driven the integration of planned conservation activities with regional
and landscape-level environmental and social initiatives. At the mine, the landscape approach currently
consists of maintaining forest connectivity between the on-site azonal habitat conservation zones (and
rehabilitated areas as these progress) and the surrounding forests. Moreover, forest connectivity between the
mine area and the Ankeniheny-Zahamena Corridor will be maintained through landscape-level designs and
interventions in line with the Durban Vision to increase the surface areas of protected areas in Madagascar;
the development of this programme is at an early stage and aims to be conducted in collaboration withConservation International. At Ankerana, the offset design is based on a phased and spatially concentric,
landscape-level approach. Long-term community needs have been identified and participative zoning has
been completed.
6. Stakeholder participation:
The Project is committed to stakeholder PARTICIPATIONand has made significant progress with local
communities and NGOs. Examples include interaction during the integration of the Ambatovy Project offset
programme with national, regional and local plans and community involvement at the heart of the zoning
project at the proposed Ankera offset site. In the latter example, a functional, participatory forest zoning
process is being implemented by the community with assistance from the Forest Services and the help oflocal NGOs. This will result in areas identified for multiple-use at the periphery of the offset site being
transferred to the community as stipulated by Malagasy law and promoted in the regional plan.
7. Equity:
While the Ambatovy Project is committed to BBOP Principles 6 and 7, insufficient data are currently available
to apply the latter strictly. As data become available, the Project will develop its cost-benefit model and
analysis using key elements of the BBOP BIODIVERSITY OFFSET COST-BENEFIT HANDBOOK5and in consultation
with stakeholders. The Project is currently in the process of establishing a strategy to implement the socio-
environmental action programme, including assessing natural resources usages by the local communities at
the Ankerana and mine sites, further to which dollar value of the losses will be determined and compensationoptions identified and provided.
8. Long-term outcomes:
The Ambatovy offset programme for the mine region, comprising on-site azonal habitat conservation,
community-based forest management, forest connectivity of mine area, Ramsar wetland management, forest
5 Available at www.forest-trends.org/biodiversityoffsetprogram/guidelines/cbh.pdf.
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corridor rehabilitation and the proposed Ankerana offset, is being designed for long-term success following its
implementation. Four activities will support the long-term outcomes:
Strong community involvement throughout the planning, designing and implementation phases with the
development of complementary sustainable activities in the surrounding agricultural matrix and in the
multiple use area of the forests surrounding the critical habitats (core areas). Appropriate joint activities are
being identified as the result of ongoing stakeholder interaction and data gathering.
Development of financial strategies, mechanisms, and commitments as the operational phase of the
Project begins (2011), based on the analysis of stakeholder needs and the Projects predicted economic
operating environment. In light of the ongoing financial crisis and the resulting economic uncertainties,
ADAPTIVE MANAGEMENTstrategies will play a key role in securing long-term financing for the Ambatovy
offset programme.
Identification of long-term governmental legal and political commitment to protect the conservation sites in
the mine region and the proposed offset site at Ankerana. A high level of commitment is expected as
elements of the mine area and the proposed offset site have been designed to fall under the future
Malagasy protected area system (SAPM), which itself is a part of the Presidential Durban commitment and
which is expected to attract significant outside funding as a result of a global concern for biodiversity.
Determining the institutional arrangements for managing the offset sites into the long-term. It has not yet
been decided how the Ankerana site will be managed, with all options remaining open, i.e., managed by
governmental institutions, by an NGO, by the community, by the company or a combination of any of the
foregoing. The on-site conservation zones forests will be managed by the Project, the FOREST
CONNECTIVITYprogramme will likely be community-based, while the Ramsar site has a defined
management structure.
9. Transparency:
The Ambatovy Projects intention to offset its residual impacts on biodiversity is a commitment developed in
the ESIA, which has undergone thorough public consultation, hearings and a public information process.Consequently, the Projects strategic environmental and social commitments are in the public domain and its
offset activities have been, and are being, scrutinised by the Malagasy environmental authorities, regional and
international NGOs, the local communities and the lender banks. Since becoming a BBOP Pilot Project,
Ambatovy has committed to ensuring that design (and ultimately implementation) activities are completed in a
transparent fashion. Transparency allows the Project to ensure stakeholders are well informed and able to
offer insightful feedback that contributes to the optimisation of conservation outcomes.
10. Science and traditional knowledge:
In order to evaluate residual impacts on biodiversity and quantify the required offset, the Project has applied
established and developing scientific methodologies. In parallel, traditional knowledge is being utilised (forexample, species identification in time and space, identification of species utilisation by humans (medicinal)
and animals (fruit trees), and land use patterns (plant-substrate relationships)).
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5. Current Status of the Projectand Offset
5.1 Project chronology and status (as of December 2008)
1960: Genim, a French company, conducts exploration drilling and identifies the Ambatovy and Analamay
nickel cobalt ore bodies; environmental considerations of the early feasibility study were very limited and
did not consider vegetation anomalies nor the importance of nearby wetland (e.g. using Torotorofotsy for
tailings disposal);
1970: Under the President of Madagascar, Didier Ratsiraka, a partnership with North Korea leads to the
analysis ofa bulk sample that confirmed the existence of nickel and cobalt but which led to no furtherdevelopment; environmental considerations were absent during exploration (e.g. no rehabilitation of test
pit, which remains unvegetated today);
1994 1997: Phelps-Dodge conducts exploration drilling and develops a feasibility study and an ESIA (not
submitted to ONE); vegetation anomaly recognised and quantified (vegetation map), biological inventories
created; management principles for surrounding forests conceptualised; importance of azonal habitats
recognised;
1998 2003: Restoration of exploration roads and platforms undertaken in light of Project development
uncertainties;
2003 2006: Dynatec conducts exploration drilling and develops a feasibility study and an ESIA; Final
Investment Decision taken by the investors (Dynatec and partners); on-site and offset conservation ideas
captured in the ESIA; Ambatovy becomes BBOP pilot Project; ESIA was permitted by ONE on December
1st, 2006; and
2007 2008: Elaboration of the Ambatovy Project thematic Environmental and Social Plans (18 plans: air,
noise, water etc and biodiversity); implementation of Biodiversity Action Plan (and others), development of
priority TAXA-specific draft management plans (lemur, Mantella species, fish and flora). Confirmation of
shareholders and loans and start of construction.
5.2 Offset chronology and status (as of December 2008)
2004 2005: Concept of biodiversity offset integrated with other Project activities, with a preliminary
survey of proposed offset site undertaken and documented in the ESIA; proposed offset site selection
based on geological, substrate, altitude and forest structure similarity (relative to principal IMPACT SITE);
2006: Ambatovy Project selected as a BBOP Pilot Project at Pretoria meeting;
2007: Participation in BBOP meetings (London and Bainbridge) and contribution to development of BBOP
handbooks and guidelines; concepts for Ankerana site management programme developed and zoning
initiated;
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2008:
Preparation of interim report outlining technical aspects of the offset process (e.g. benchmark
selection, confirmation of impacts, preliminary loss calculations and completed Key Biodiversity
Components Matrix (KBCM);
Preparation of supplementary report with revised benchmark selection and loss calculations, includingupdated KBCM with quantitative species data;
Preparation of complementary field work (terrestrial fauna) in response to gap analysis; inclusion of other
Project components (pipeline, tailings, plant and harbour) in overall assessment of residual impacts;
Implementation of Ankerana site management programme:
Stakeholder consultations (local communities, NGOs and government including Office National
lEnvironnement (ONE,) Forestry Department, Gendarmerie, District of Brickaville, local mayors and
police forces);
Reforestation work on periphery area of proposed offset; this focused mainly on planting wood for
construction uses to avoid primary forest logging in the offset area;
Population awareness campaigns around the proposed offset, conducted by field teams and
partners. The objectives of the campaigns were to define the offset site boundary and explain
existing laws that prohibit forest clearance;
Support provided to the mixed brigade (includes local communities, NGOs, local administrative staff
and the police force) which manages forestry resource exploitation through out the local communes;
Financial and logistic support to update the five year Communal Development Plans for impacted
communes; and
Technical committee meeting with SAPM focusing on integration of the proposed offset site with the
national protected areas network.
Conceptualised and pending (for 2009):
The offset design work, following guidance in the BBOP BIODIVERSITY OFFSET DESIGN HANDBOOKhas to
date quantified biodiversity losses as presented below. The next phase of work will be to calculate
offset gains and continue with the design of the offset and offset activity plan;
The proposed Ankerana offset site has undergone only preliminary characterisation. Detailed baseline
ecological characterisation is planned for 2009 focusing on ecosystems, habitats, fauna, flora and
socioeconomic attributes. This information will underpin the calculation of offset gains;
Socio-environmental losses will be defined and subsequently an appropriate compensation calculation
strategy and programme will be designed; and
Continued interaction with stakeholders to refine and enhance the offset activity plan.
In summary, the Project is committed to designing and financing a long-term offset programme that aims at
achieving NO NET LOSSon biodiversity and preferably NET GAIN. Substantial progress has been made by
calculating the residual impacts on biodiversity and identifying potential offset mechanisms. Ambatovy will
continue to work closely with stakeholders on the offset design and plan the financial mechanisms to secure
the offsets in the long-term, using adaptive management in response to the insecurities of the global financial
crisis. The following pages of this case study detail the actions conducted and those that are planned for the
future.
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6. Business Case for aBiodiversity Offset
The vision of the Ambatovy Project is stated as follows: The Ambatovy partnership will develop and operate a
sustainable nickel / cobalt mining and processing enterprise that significantly contributes to our host country,
delivers outstanding safety, environmental and social records and generates attractive economic returns.
The environmental strategy designed to honour the Projects vision to deliver outstanding environmental
records consists of:
Ensuring full regulatory compliance and conformity with international loan agreements;
Minimising residual impacts through the stringent application of the mitigation hierarchy;
Reducing environmental risks through dynamic management guided by Malagasy know-how and
stakeholder consultation; and
Producing positive CONSERVATION OUTCOMESon biodiversity through the offset programme that aims at
achieving no net loss on biodiversity, and possibly net gain, in order to sustain a good citizen project
status in a host country recognised as constituting a biodiversity hotspot.
The business benefit of its offset programme is essentially linked to risk management. As a world class mining
project, Ambatovy and its shareholders believe in demonstrating good environmental management practices
to secure its license to operate. To Ambatovy, a license to operate consists of the permanent support of civil
society, local communities, national and international NGOs and governmental authorities in the mannersocial and environmental affaires are managed. Because Madagascars biodiversity is universally considered
of utmost importance by national and international STAKEHOLDERSproducing positive conservation outcomes
that offset the residual impacts on biodiversity is a critical component of this license to operate.
It is recognised by the Projects shareholders that the Ambatovy offset programme has provided additional
confidence to the lender banks in securing access to capital. This has created reputational benefits to the
shareholders that can result in easier access to land, human and financial resources for future projects in
Madagascar and elsewhere in the world. It is expected that this approach will result in competitive advantage
for the shareholders in relation to other governments.
Conversely, bad environmental practice is bound to produce higher operating costs, expensive permit delays,liabilities, and lost revenues. Consequently, engaging in good environmental practice will maximise the overall
long-term economic return to shareholders, stakeholders and government.
It is worth mentioning that the Malagasy governmental policy, through the Madagascar Action Plan, refers to
biodiversity offsets. The Ambatovy offset programme under the BBOP guidance is thus aligned with
Madagascars endeavour to protect its unique biodiversity heritage.
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In summary, Ambatovy believes that its offset programme will bring about the following advantages:
Continuing access to land and capital;
Increasing investor confidence and loyalty;
Reducing risks and liabilities;
Strengthening relationships with local communities, government regulators, environmental groups andother stakeholders;
Building trust on a credible reputation for environmental and biodiversity related management performance
and winning a social license to operate;
Increasing regulatory goodwill which leads to faster permitting;
Influencing emerging environmental regulation and policy;
Developing more cost effective means of complying with increasingly stringent environmental regulations;
Taking advantage of first mover benefits in the marketplace Madagascar;
Maximising strategic opportunities in the new markets and businesses emerging as biodiversity offsetsbecome more widespread; and
Improving staff loyalty.
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7. The Offset Design Process
7.1 Guidance and methodologies used
The Ambatovy biodiversity offset programme has been developed as an iterative process calling upon BBOP
principles and guidance. Additional inputs towards the development of the Projects offset programme came
from a number of recent good practice guides, including Good Practice Guidance for Mining and Biodiversity
(International Council on Mining and Metals 2006), Planning for Integrated Mine Closure: Toolkit(International
Council on Mining and Metals 2008), Performance Standard 6: Biodiversity Conservation and Sustainable
Natural Resource Management(International Finance Corporation 2006) and Biodiversity Offsets: Views,
Experience, and the Business Case (ten Kate et al. 2004).
The BBOP guidance supports the development of either single or COMPOSITE OFFSETsites to compensate forresidual impacts on biodiversity. The Ambatovy offsets programme is multifaceted because it is a large project
with many components (see Section 3.2). While the design and implementation of the several components of
the Ambatovy offset programme has progressed, the predicted conservation outcomes from these various
offset components have not yet been fully calculated. Meanwhile, Ambatovy has focused on its proposed
Ankerana offset as the most significant component of its offset. The proposed Ankerana offset design is
based on the guidance in the draft BBOP Biodiversity Offset Design Handbook revised in December 2008
(available at www.forest-trends.org/biodiversityoffsetprogram/guidelines/odh.pdf). However, the high
degree of social sensitivity around Ankerana has led the project to undertake community involvement before
the planned biodiversity assessment at the site.
7.2 Roles and responsibility
The Ambatovy offset programme is designed, implemented and financially supported by the Ambatovy
Project. The offset commitment was reiterated by Sherritt Incorporated, the Projects operator, in November
2008 during a clarification meeting with the BBOP Secretariat and representatives of Forest Trends, CI and
WCS. The offset programme is managed and monitored by the Projects environmental department. Since
Ambatovy became a BBOP Pilot Project, the BBOP Secretariat and members of the BBOP Advisory
Committee have also monitored progress. Senior Project representatives attend all BBOP meetings and
provide updates and feedback to the BBOP Secretariat. The Projects BBOP team includes:
A focal point (Pierre O. Berner, Environmental Director, Ambatovy Project);
A full time consultant responsible for supporting the offset programme management implementation
(Steven Dickinson of Golder Associates / Ambatovy Project);
An ecological assessment consultant responsible for the benchmark, loss and gain calculations (Aristide
Andrianarimisa of WCS); and
Environmental superintendent (monsieur Alphonse) leading a technical environmental and social field team
responsible for social and environmental management at the proposed Ankerana offset site. This team led
consultations with local stakeholders, including local communities, local forestry and police authorities and
local NGOs. A legal team is supporting the superintendent to ensure the legal protection status of the
Ankerana site.
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7.3 The offset design process
7.3.1 Step 1: Review project scope and activities
The nature, scope and geographical location of the Ambatovy offset programme was outlined in the ESIA as a
COMPENSATIONmeasure that would go above and beyond the expected regulatory commitments. The basic
Ambatovy offset concept was presented and discussed in the many stakeholder public information meetings
associated with the ESIA review. As Ambatovy was accepted as a BBOP Pilot project in 2006, a more
structured approach was developed, which led to the multifaceted programme outlined in Section 3.2.
7.3.2 Step 2: Review the legal framework and / or policy context for a biodiversity offset
The key elements of the legal framework and policy context for the Ambatovy Projects biodiversity offset
programme comprise the MECIE decree, the Madagascar Action Plan (MAP) 2007 2012, the regional and
communal development plans and the EQUATOR PRINCIPLES. Further information on these and other regulatory
requirements is provided in Section 2.1.
7.3.3 Step 3: Initiate a stakeholder participation process
As noted previously, the Ambatovy Project obtained its permit from the Malagasy regulatory authorities in
December 2006, based on a large ESIA that involved public information, consultation and enquiry throughout
the development and review process. Subsequently stakeholder consultations have been central to
discussions on integrating the offset programme with national, regional and local plans. At the Ankerana offset
site, the community buy-in process is progressing well and precedes the hard-core biological assessment that
can only be conducted after full community participation is demonstrated.
The offset stakeholder participation process can be summarised as:
Confirming key stakeholders (the JV partners, government, financiers, NGOs and local communities, see
Section 2.3);
Engaging stakeholders in the offset design process by presenting and discussing the offsets objectives
and the proposed implementation process;
Engaging communities in the offset design process by assessing the impact the offset will bring about and
agreeing on an acceptable MITIGATIONstrategy; and
Integrating stakeholder feedback into the design process, especially with respect to land use in the multiple
use areas (site zoning); this part of the process is in its initial stage and will continue throughout the offset
zoning processes.
7.3.4 Step 4: Determine the need for an offset based on residual adverse effects
This section describes how the Ambatovy offset planning team:
1. Assessed the likely impacts on biodiversity caused by the Ambatovy Project;
2. Prepared a Key Biodiversity Components Matrix (KBCM);
3. Applied the mitigation hierarchy;
4. Determined residual impacts; and
5. Checked whether these residual impacts could be offset.
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7.3.4.1 Assessing biodiversity impacts
Biodiversity impacts are presented in the Projects 2006 ESIA. The ESIA BASELINEand impact analysis
(including CUMULATIVE IMPACTS) followed World Bank (IFC, International Finance Corporation) standards.
A formal summary is available at:
http://www.sherritt.com/doc08/files/coal/abatovy/EAAmbatovy_EnglishSummary.pdf.
Details of the biodiversity impacts are available in Volume J of the full ESIA report (full document available in
French or English, on CD, through the Ambatovy Project or the Malagasy Ministry for Environment).
The Projects main impacts will occur at the mine site, through the progressive clearing of the mine footprint
(total footprint of 2,126 hectares, of which 1,336 ha will result from clearance and the balance resulting from
indirect (edge effect) impacts around the cleared area) located within an ecologically sensitive natural forest
mosaic of the eastern mid-altitudinal forest corridor. Stringent impact avoidance and minimisation strategies
were applied in the design phase of the Project, so RESIDUAL IMPACTSon biodiversity from the other key
Project components, most of which lie in heavily degraded areas, are of less significance (but will nonetheless
be offset). These include pipelines, the processing plant and refinery, tailings management facility and pier
extension (see Section 3 for a summary of associated impacts).
As the Project has evolved, spe